Field of the Invention
[0001] The present invention is a process for regenerating an oxidized magnesium sulfate-containing
aqueous medium from a sulfur-dioxide removal process for removing sulfur dioxide from
a gaseous stream, and a process for removing sulfur dioxide from a sulfur dioxide-containing
gaseous stream in a wet scrubbing unit, using magnesium hydroxide and magnesium sulfite,
where the spent aqueous scrubbing liquor is oxidized and then regenerated by addition
of lime.
Background of the Invention
[0002] Processes have been devised to remove sulfur dioxide from a sulfur dioxide-containing
gas, such as combustion off gases from a power plant, where magnesium-containing scrubbing
components are used to react with and remove the sulfur dioxide.
[0003] One such process uses an aqueous solution of magnesium hydroxide and/or magnesium
sulfite which reacts with the sulfur dioxide to produce magnesium sulfite from magnesium
hydroxide present and magnesium bisulfite from magnesium sulfite present by the following
reactions:


and

[0004] A portion of the scrubbing solution in the wet scrubbing unit is removed and replaced
by fresh scrubbing component-containing aqueous solution. The portion of aqueous scrubbing
solution removed from the wet scrubbing unit contains magnesium sulfite and magnesium
bisulfite and is passed to an oxidizing unit where the magnesium sulfite and magnesium
bisulfite are oxidized to magnesium sulfate, by the following equations:

and

[0005] The magnesium sulfate, so produced, remains in the aqueous solution and is next subjected
to a regeneration step where lime for regeneration is added to the magnesium sulfate-containing
aqueous solution to form solid calcium sulfate (gypsum) and magnesium hydroxide, by
the following equation:

with the solid calcium sulfate precipitating from the aqueous solution. The solid
calcium sulfate is then removed from the aqueous solution and magnesium hydroxide
in the aqueous solution may be recycled to the wet scrubbing unit for use in removal
of further sulfur dioxide from a gaseous stream.
[0006] Such magnesium based sulfur dioxide wet scrubbing processes are described, for example,
in U.S. 5,039,499; U.S. 5,084,255; and U.S. 5,270,026, all of which are assigned to
the assignee of the present invention and the contents of said patents are incorporated
by reference herein.
[0007] Another such process uses a magnesium-enhanced lime slurry which reacts with the
sulfur dioxide to produce solid calcium sulfite from the lime and magnesium sulfite
and magnesium bisulfite from the magnesium ions present in the magnesium-enhanced
lime slurry. A portion of the scrubbing medium is removed from the wet scrubbing unit
and replaced by fresh magnesium-enhanced lime slurry. The portion of the aqueous scrubbing
medium removed from the wet scrubbing unit contains solid calcium sulfite and dissolved
magnesium sulfite and magnesium bisulfite and is passed to an oxidizing unit where
the calcium sulfite is oxidized to solid calcium sulfate, and the magnesium sulfite
and magnesium bisulfite oxidized to magnesium sulfate. The solid calcium sulfate is
removed from the aqueous medium and the resultant magnesium sulfate, so produced,
remains in the aqueous solution and is next subjected to a regeneration step where
lime for regeneration is added to the magnesium sulfate-containing aqueous solution
to form additional solid calcium sulfate and magnesium hydroxide, with the additional
solid calcium sulfate precipitating from the aqueous solution. The additional solid
calcium sulfate is then removed and magnesium hydroxide may be recycled for use as
further magnesium-enhanced lime slurry for removal of sulfur dioxide from a gaseous
stream.
[0008] Such magnesium-enhanced lime scrubbing processes are described, for example, in U.S.
3,914,378; U.S. 3,919,393; 3,919,394; 4,976,936; and 4,996,032, all of which are assigned
to the assignee of the present invention and the contents of said patents are incorporated
by reference herein.
[0009] While such processes have been found to be very useful in removing sulfur dioxide
from gaseous streams, a problem can arise in situations where gypsum and calcium carbonate
scales can form in process lines and equipment downstream from the regeneration tank.
It is believed that the primary cause of such scaling is due to over-dosing of lime
for regeneration fed to the magnesium sulfate solution in the regeneration tank, which
is often operated at a pH level of between about 10-11. Such overdosing subsequently
raises the pH and calcium ion levels in the downstream process lines and equipment,
with the formation of scale, and resulting scaling, which is predominantly gypsum
scaling with sometimes minor amounts of calcium carbonate scaling.
OBJECTS OF THE INVENTION
[0010] It is an object of the present invention to provide a process for regenerating an
oxidized magnesium sulfate-containing aqueous medium from a sulfur-dioxide removal
process so as to prevent scaling of lines and equipment downstream of the regeneration
tank wherein lime for regeneration is added to the magnesium sulfate-containing aqueous
solution.
[0011] It is another object of the present invention to provide a magnesium based or magnesium-enhanced
lime scrubbing process using a wet scrubbing unit where the process is operated in
a manner so as to prevent scaling of lines and equipment downstream of a regeneration
tank wherein lime for regeneration is added to a magnesium sulfate-containing aqueous
solution.
SUMMARY OF THE INVENTION
[0012] The present process regenerates an oxidized magnesium sulfate-containing aqueous
medium from a sulfur dioxide removal process where a magnesium-containing aqueous
scrubbing medium is used in a wet scrubbing unit, and a portion of the aqueous scrubbing
medium containing magnesium sulfite and magnesium bisulfite is removed from the wet
scrubbing unit and passed to an oxidizer where the magnesium sulfite and magnesium
bisulfite are oxidized to magnesium sulfate. The oxidized aqueous scrubbing solution
is then passed to a regeneration tank and an aqueous lime slurry is fed to the regeneration
tank for reaction with the magnesium sulfate, with concomitant production of solid
calcium sulfate and magnesium hydroxide, which are discharged from the regeneration
tank. The aqueous lime slurry for regeneration is added to the magnesium sulfate solution
in the regeneration tank in an amount sufficient to maintain the aqueous solution
discharged from the regeneration tank at a pH of between 9.0 - 9.5, a magnesium ion
content in the aqueous solution of between about 200 - 600 ppm, (parts per million)
and a calcium ion content in the aqueous solution of between about 2000 - 2500 ppm.
The solid calcium sulfate and magnesium hydroxide is then separated from the discharged
aqueous solution for further processing and at least a portion of the aqueous solution
may be returned to the wet scrubbing unit.
[0013] The present process also provides for desulfurizing of a sulfur dioxide-containing
gaseous stream by contacting the gas stream with an aqueous medium containing a scrubbing
compound selected from magnesium sulfite and magnesium hydroxide, in a wet scrubbing
unit, to remove sulfur dioxide through production of magnesium sulfite and magnesium
bisulfite, and removing a portion of the aqueous scrubbing medium from the wet scrubbing
unit. The magnesium sulfite and magnesium bisulfite are then oxidized to magnesium
sulfate. The oxidized aqueous scrubbing medium, containing magnesium sulfate, is then
passed to a regeneration tank and regenerated according to the present process.
[0014] In another embodiment of the present process for desulfurizing of a sulfur dioxide-containing
gaseous stream, the aqueous scrubbing medium is a magnesium-enhanced lime slurry,
with calcium sulfite, as well as magnesium sulfite and magnesium bisulfite produced
in the wet scrubbing unit, with a portion of the aqueous scrubbing medium removed
from the wet scrubbing unit. The removed portion, containing solid calcium sulfite
and dissolved magnesium sulfite and magnesium bisulfite, is oxidized to produce solid
calcium sulfate and dissolved magnesium sulfate. The solid calcium sulfate is removed
from the aqueous medium and the oxidized aqueous scrubbing medium, containing magnesium
sulfate, is then passed to a regeneration tank and regenerated according to the present
process.
[0015] In a further embodiment of the present process for desulfurizing of a sulfur dioxide-containing
gaseous stream, the oxidized discharge from the oxidation unit is processed so as
to provide a high purity magnesium hydroxide by-product.
DESCRIPTION OF THE DRAWINGS
[0016] The invention will become more readily apparent from the following description of
preferred embodiments thereof shown, by way of example only, in the accompanying drawings,
wherein:
Figure 1 is a schematic illustration of the present process for regenerating an oxidized
magnesium sulfate-containing medium from a sulfur-dioxide removal process according
to the present invention;
Figure 2 is a schematic illustration of a sulfur dioxide removal process according
to the present invention using a solution of magnesium sulfite and magnesium bisulfite
in a wet scrubbing unit;
Figure 3 is a schematic illustration of a sulfur dioxide removal process according
to the present invention using a magnesium-enhanced lime slurry in a wet scrubbing
unit; and
Figure 4 is a schematic illustration of a sulfur dioxide removal process according
to the present invention where the discharge from the oxidizing unit is processed
to provide a high-purity magnesium hydroxide by-product.
DETAILED DESCRIPTION
[0017] The present process provides for regeneration of an oxidized magnesium sulfate-containing
aqueous solution from a sulfur dioxide wet scrubbing process which prevents scaling
of lines and equipment downstream of a regeneration tank wherein lime for regeneration
is added to the magnesium sulfate-containing aqueous solution to produce calcium sulfate,
which precipitates from the aqueous solution, and magnesium hydroxide.
[0018] The schematic illustration of Figure 1 shows the present process for regenerating
an oxidized magnesium sulfate-containing aqueous medium from a sulfur dioxide removal
process. As shown, an aqueous medium from a sulfur dioxide removal system, which has
been oxidized, and contains magnesium sulfate in solution, is passed through line
1 to a regeneration tank 2. An aqueous lime slurry, from a source 3 is fed to regeneration
tank 2 through line 4 and reacts with magnesium sulfate present in the aqueous solution
to produce solid calcium sulfate and magnesium hydroxide. The resultant mixture is
passed through line 5 to a downstream solids separator 6. In a solids separator 6,
the solid calcium sulfate (gypsum) is removed and discharged through line 7 for use
or disposal, while the aqueous medium containing magnesium hydroxide is removed through
line 8.
[0019] It is critical to the present process that the lime from source 3 be added to the
regeneration tank 2 in an amount sufficient such that the aqueous solution discharged
from the regeneration tank 2 through line 5 is maintained at a pH of between 9.0-9.5,
a magnesium ion content in the aqueous solution of between about 200-600 ppm, and
a calcium ion content in the aqueous solution of between about 2000-2500 ppm.
[0020] The pH of the aqueous solution discharged from the regeneration tank 2 must be between
9.0-9.5. If a pH of less than 9.0 is used, insufficient magnesium hydroxide precipitation
occurs, while if a pH of greater than 9.5 is used, an increase in gypsum relative
saturation results, with subsequent gypsum scaling. Preferably, the pH is maintained
at a value of between about 9.1 - 9.3.
[0021] The magnesium ion content (Mg++) in the aqueous solution discharged from the regeneration
tank 2 must be at a value of about 200-600 ppm, preferably between about 200-400 ppm.
If less than about 200 ppm is present, calcium levels become greater than 2500 ppm
which leads to gypsum scaling, while if greater than about 600 ppm is present, the
magnesium hydroxide is not sufficiently precipitated from the solution.
[0022] The calcium ion content (Ca++) in the aqueous solution discharged from the regeneration
tank 2 must be at a value of about 2000-2500 ppm, preferably between about 2100-2300
ppm. If less than about 2000 ppm is present, insufficient gypsum is precipitated,
leaving sulfate levels >1200 ppm which also leads to gypsum scaling, while if greater
than about 2500 ppm is present, danger of saturation and scaling due to gypsum formation
from high calcium levels is a problem.
[0023] This, control of magnesium levels exiting the regeneration tank to 200-600 ppm discourages
gypsum scaling of downstream process lines by suppressing saturation levels of both
calcium and sulfate ions in the exiting liquor.
[0024] In one embodiment of a sulfur dioxide removal process of the present invention, a
magnesium-containing aqueous scrubbing medium used in the wet scrubbing unit is a
magnesium-containing aqueous scrubbing solution containing a scrubbing compound selected
from magnesium sulfite and magnesium hydroxide that contacts the sulfur dioxide-containing
gas to remove sulfur dioxide through production of magnesium bisulfite from magnesium
sulfite and magnesium sulfite from magnesium hydroxide. A portion of the aqueous scrubbing
solution, containing magnesium sulfite and magnesium bisulfite is removed from the
wet scrubbing unit and passed to an oxidizer where the magnesium sulfite and magnesium
bisulfite are oxidized to magnesium sulfate from an aqueous solution of magnesium
sulfate. The aqueous solution of magnesium sulfate is then passed to a regeneration
tank and contacted with a lime slurry as above described.
[0025] In another embodiment of a sulfur dioxide removal process of the present invention,
a magnesium-enhanced lime scrubbing aqueous slurry is used in the wet scrubbing unit
that contacts the sulfur dioxide-containing gas to remove sulfur dioxide through production
of calcium sulfite, in addition to magnesium sulfite and magnesium bisulfite. A portion
of the aqueous scrubbing slurry containing calcium sulfite, magnesium bisulfite and
magnesium bisulfite is removed from the wet scrubbing unit and passed to an oxidizer
where the calcium sulfite is oxidized to calcium sulfate and the magnesium sulfite
and magnesium bisulfite are oxidized to magnesium sulfate. The calcium sulfate, a
solid, is removed from the aqueous medium and the magnesium sulfate, in aqueous solution
is then passed to a regeneration tank and contacted with a lime slurry as above described.
[0026] Referring now to Figure 2, which schematically illustrates the first embodiment of
a sulfur dioxide removal process, there is shown a wet scrubbing unit 9 to which a
sulfur dioxide-containing gas is charged though line 10, the gas contacts an aqueous
solution containing magnesium sulfite or magnesium hydroxide fed thereto through line
11, with the sulfur dioxide removed from the gas by production of magnesium sulfite
from magnesium hydroxide present and magnesium bisulfite from magnesium sulfite present,
with clean gas discharged through line 12. A recycle of the wet scrubbing unit contents
is effected by means of a pump 13 in recycle line 14, while a portion of the aqueous
scrubbing solution is removed through valve 15. The portion of removed aqueous solution,
removed through valve 15, which contains magnesium sulfite and magnesium bisulfite,
passes through line 16 to an oxidizing unit 17. The removed aqueous solution is contacted
in the oxidizing unit 17 with an oxygen-containing gas, such as air, fed through line
18, with off-gases discharged through line 19, so as to oxidize magnesium sulfite
and magnesium bisulfite present in the aqueous solution to magnesium sulfate. The
oxidized aqueous scrubbing solution, containing magnesium sulfate, is then passed
through line 20 to a regeneration tank 21. An aqueous slurry of lime, from a source
22 is fed to the regeneration tank 21 through line 23 and reacts with the magnesium
sulfate present in the aqueous solution therein to produce solid calcium sulfate and
magnesium hydroxide. The lime slurry is added in an amount to maintain the aqueous
solution in line 24 at a pH of between 9.0-9.5, a magnesium ion content of about 200
to 600 ppm, and a calcium ion content of about 2000-2500 ppm. The resultant mixture
is fed through line 24 to a solids separator 25, where solid calcium sulfate is separated
and removed from the aqueous solution and discharged through line 26, while the aqueous
solution is removed through line 27. All or a portion of the removed aqueous solution
may be returned to the wet scrubbing unit 9, preferably by means of line 28, which
feeds into line 11 to the wet scrubbing unit 9.
[0027] Referring now to Figure 3, there is schematically illustrated another embodiment
of a sulfur dioxide wet scrubbing removal process where a magnesium enhanced aqueous
lime slurry is used as the aqueous scrubbing medium in a wet scrubbing unit. As illustrated,
a wet scrubbing unit 29 is provided to which a sulfur dioxide-containing gas is charged
through line 30. The gas contacts a magnesium-enhanced aqueous lime slurry, containing
lime and magnesium hydroxide fed to the wet scrubber 29 through line 31, with the
sulfur dioxide removed from the gas by reaction with lime to form calcium sulfite,
magnesium sulfite by reaction with magnesium hydroxide, and magnesium bisulfite from
magnesium sulfite present, with clean gas discharged through line 32. A recycle of
the wet scrubbing unit contents is effected by means of pump 33 in recycle line 34,
while a portion of the aqueous scrubbing medium is removed through valve 35. The portion
of removed aqueous medium removed through valve 35, passes through line 36 to a solids
separator 37. In the solids separator 37, solid calcium sulfite is separated from
the aqueous medium and discharged through line 38, while the clarified aqueous medium,
a solution of magnesium sulfite and magnesium bisulfite is passed through line 39
to an oxidizer unit 40. The removed aqueous solution is contacted in the oxidizing
unit 40 with an oxygen-containing gas, such as air, fed through line 41 with off-gases
discharged through line 42, so as to oxidize magnesium sulfite and magnesium sulfate
present in the aqueous solution to magnesium sulfate. The oxidized aqueous scrubbing
solution, containing magnesium sulfate, is then passed through line 43 to a regeneration
tank 44. An aqueous slurry of lime, from a source 45 is fed to the regeneration tank
44 through line 46 and reacts with the magnesium sulfate present in the aqueous solution
therein to produce solid calcium sulfate and magnesium hydroxide. The lime slurry
is added in an amount to maintain the aqueous solution discharged through line 47
at a pH of between about 9.0-9.5, a magnesium ion content of about 200 to 600 ppm,
and a calcium ion content of about 2000-2500 ppm. The resultant mixture is fed through
line 47 to a second solids separator 48, where solid calcium sulfate is separated
and removed from the aqueous solution and discharged through line 49, while a portion
of the aqueous solution is removed through line 50. All, or a portion of the removal
aqueous solution may be returned to the wet scrubbing unit 29, preferably by means
of line 51, which may feed into line 31 to the wet scrubbing unit 29.
[0028] In a further embodiment of the process of the present invention illustrated in Figure
4, an aqueous medium from a wet-scrubbing unit as described in Figure 3, and containing
magnesium sulfite and/or magnesium bisulfite and calcium sulfite is fed through a
line 52 to an oxidizing unit 53 and contacted with an oxygen-containing gas fed through
line 54, with off gases discharged through line 55. The oxidized aqueous medium, containing
magnesium sulfate and calcium sulfate (gypsum) is passed through line 56 to a first
solids separator 57, such as a hydroclone, where calcium sulfate solids are separated
and removed through line 58 and passed to a filter 59. Gypsum product is recovered
through line 60. The aqueous medium from first solids separator 57 is removed through
line 61, and contains magnesium sulfate and some residual calcium sulfate, and is
charged to a second solids separator 62. Aqueous filtrate from filter 59 may also
be charged to the second solids separator 62 through line 63. Solids from second solids
separator, primarily calcium sulfate and removed through line 64, while the aqueous
medium containing primarily magnesium sulfate is discharged through line 65. The aqueous
medium from line 65 may be returned to the wet scrubbing unit, or a portion thereof
may be directed through line 66 to a regeneration tank 67. In regeneration tank 67,
the aqueous medium containing magnesium sulfate is contacted with an aqueous lime
slurry, such as an aqueous slurry of dolomitic low silica lime, fed through line 68.
The lime slurry is added in an amount to maintain the aqueous solution discharged
through line 69 at a pH of between 9.0-9.5, a magnesium ion content of about 200 to
600 ppm, and a calcium ion content of about 2000-2500 ppm. The resultant mixture is
fed to a third solids separator 70 through line 69, where solid calcium sulfate is
separated and removed from the aqueous medium and discharged through line 71 and may
be fed to filter 59. The aqueous medium, containing a high purity magnesium hydroxide,
is removed through line 72 and fed to a magnesium hydroxide collection unit 73. This
is an excellent source of high-purity magnesium hydroxide.
1. A process for regenerating an oxidized magnesium sulfate-containing aqueous medium
from a sulfur-dioxide removal process for removing sulfur dioxide from a gaseous stream,
so as to remove scale-forming components from the aqueous medium and prevent scaling
of lines and equipment downstream from a regeneration tank where lime for regeneration
is added to the magnesium sulfate-containing aqueous medium in the regeneration tank,
for reaction with the magnesium sulfate, to produce solid calcium sulfate and magnesium
hydroxide; comprising:
discharging solid calcium sulfate, magnesium hydroxide and aqueous solution from the
regeneration tank, while adding the lime for regeneration to the regeneration tank
in an amount sufficient to maintain the aqueous solution discharged at a pH of between
9.0 - 9.5, a magnesium ion content in the aqueous solution of between about 200 -
600 ppm, and a calcium ion content in the aqueous solution of between about 2000 -
2500 ppm; and
separating solid calcium sulfate from the aqueous solution.
2. The process for regenerating an oxidized magnesium sulfate-containing aqueous medium
from a sulfur-dioxide removal process as defined in Claim 1 wherein the pH of the
aqueous solution discharged from the regeneration tank is between 9.1 - 9.3.
3. The process for regenerating an oxidized magnesium sulfate-containing aqueous medium
from a sulfur-dioxide removal process as defined in Claim 1, wherein the magnesium
ion content in the aqueous solution discharged from the regeneration tank is between
about 200 - 400 ppm.
4. The process for regenerating an oxidized magnesium sulfate-containing aqueous medium
from a sulfur-dioxide removal process as defined in Claim 1, wherein the calcium ion
content in the aqueous solution discharged from the regeneration tank is between about
2100 to 2300 ppm.
5. The process for regenerating an oxidized magnesium sulfate-containing aqueous medium
from a sulfur-dioxide removal process as defined in Claim 1, wherein at least a portion
of the aqueous scrubbing solution, after removal of calcium sulfate, is returned to
a wet scrubbing unit for removal of sulfur dioxide from a sulfur dioxide-containing
gas.
6. A process for regenerating an oxidized magnesium sulfate-containing aqueous medium
from a sulfur-dioxide removal process for removing sulfur dioxide from a gaseous stream,
so as to remove scale-forming components from the aqueous medium and prevent scaling
of lines and equipment downstream from a regeneration tank where lime for regeneration
is added to the magnesium sulfate-containing aqueous medium in a regeneration tank,
for reaction with the magnesium sulfate, to produce solid calcium sulfate and magnesium
hydroxide; comprising:
discharging solid calcium sulfate, magnesium hydroxide and aqueous solution form the
regeneration tank, while adding the lime for regeneration to the regeneration tank
in an amount sufficient to maintain the aqueous solution discharged at a pH of between
9.1-9.3, a magnesium ion content in the aqueous solution of between about 200 - 400
ppm, and a calcium ion content in the aqueous solution of between about 2100 - 2300
ppm; and
separating solid calcium sulfate from the aqueous solution.
7. The process for regenerating an oxidized magnesium sulfate-containing aqueous medium
from a sulfur-dioxide removal process as defined in Claim 6, wherein at least a portion
of the aqueous scrubbing solution, after removal of calcium sulfate, is returned to
a wet scrubbing unit for removal of sulfur dioxide from a sulfur dioxide-containing
gas.
8. A process for desulfurizing a sulfur dioxide-containing gas comprising:
contacting a sulfur dioxide-containing gas with an aqueous medium containing a scrubbing
compound, selected from magnesium sulfite and magnesium hydroxide, in a wet scrubbing
unit to remove sulfur dioxide therefrom through production of magnesium sulfite and
magnesium bisulfite;
removing a portion of the aqueous scrubbing medium containing magnesium sulfite and
magnesium bisulfite from the wet scrubbing unit;
oxidizing the removed portion of aqueous scrubbing medium to convert magnesium sulfite
and magnesium bisulfite therein to magnesium sulfate;
passing the oxidized aqueous scrubbing medium, containing magnesium sulfate, to a
regeneration tank;
adding lime to the regeneration tank, for reaction with the magnesium sulfate, to
produce solid calcium sulfate and magnesium hydroxide;
discharging solid calcium sulfate, magnesium hydroxide and aqueous solution from the
regeneration tank, while adding the lime to the regeneration tank in an amount sufficient
to maintain the aqueous solution discharged at a pH of between 9.0 - 9.5, a magnesium
ion content in the aqueous solution of between about 200 - 600 ppm, and a calcium
ion content in the aqueous solution of between about 2000 - 2500 ppm; and
separating solid calcium sulfate from the aqueous solution.
9. The process for desulfurizing a sulfur dioxide containing gas as defined in Claim
8 wherein the pH of the aqueous solution discharged from the regeneration tank is
between 9.1 - 9.3.
10. The process for desulfurizing a sulfur dioxide-containing gas as defined in Claim
8, wherein the magnesium ion content in the aqueous solution discharged from the regeneration
tank is between about 200 - 400 ppm.
11. The process for desulfurizing a sulfur dioxide-containing gas as defined in Claim
8, wherein the calcium ion content in the aqueous solution discharged from the regeneration
tank is between about 2100 to 2300 ppm.
12. The process for desulfurizing a sulfur dioxide-containing gas as defined in Claim
8, wherein at least a portion of the aqueous scrubbing solution, after removal of
calcium sulfate, is returned to the wet scrubbing unit.
13. The process for desulfurizing a sulfur dioxide containing gas as defined in Claim
8 wherein said aqueous medium contains, in addition to magnesium sulfite and magnesium
hydroxide, lime, as an aqueous slurry, and wherein sulfur dioxide is removed through
production of calcium sulfite in addition to magnesium sulfite and magnesium bisulfite,
and wherein said calcium sulfite is separated from said removed portion of aqueous
scrubbing medium prior to said oxidizing.
14. The process for desulfurizing a sulfur dioxide containing gas as defined in Claim
13 wherein the pH of the aqueous solution discharged from the regeneration tank is
between 9.1 - 9.3.
15. The process for desulfurizing a sulfur dioxide-containing gas as defined in Claim
13, wherein the magnesium ion content in the aqueous solution discharged from the
regeneration tank is between about 200 - 400 ppm.
16. The process for desulfurizing a sulfur dioxide-containing gas as defined in Claim
13, wherein the calcium ion content in the aqueous solution discharged from the regeneration
tank is between about 2100 to 2300 ppm.
17. The process for desulfurizing a sulfur dioxide-containing gas as defined in Claim
13, wherein at least a portion of the aqueous scrubbing solution, after removal of
calcium sulfate, is returned to the wet scrubbing unit.
18. The process for desulfurizing a sulfur dioxide containing gas as defined in Claim
8, wherein said aqueous medium contains, in addition to magnesium sulfite and magnesium
hydroxide, lime, as an aqueous slurry, and wherein sulfur dioxide is removed through
production of calcium sulfite and magnesium bisulfite, and wherein the oxidized aqueous
medium contains calcium sulfate and magnesium sulfate, and calcium sulfate from calcium
sulfite of said wet scrubbing unit is removed therefrom prior to passage said oxidized
aqueous medium, containing magnesium sulfate, to said regeneration tank.
19. The process for desulfurizing a sulfur dioxide containing gas as defined in Claim
18, wherein a portion of the magnesium sulfate aqueous medium, after separation of
said calcium sulfate of said wet scrubbing unit and prior to passage to said regeneration
tank is returned to said wet scrubbing unit.
20. The process for desulfurizing a sulfur dioxide containing gas as defined in Claim
18, wherein said lime, added as a lime slurry to said regeneration tank comprises
a low silica-content magnesium-enhanced lime.
21. The process for desulfurizing a sulfur dioxide containing gas as defined in Claim
20, wherein solid calcium sulfate removed from the aqueous solution discharged from
said regeneration tank is combined with calcium sulfate removed from said oxidized
aqueous medium prior to passage to said regeneration tank.